US5928981A - Diesel catalytic converter - Google Patents

Diesel catalytic converter Download PDF

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Publication number
US5928981A
US5928981A US08/838,846 US83884697A US5928981A US 5928981 A US5928981 A US 5928981A US 83884697 A US83884697 A US 83884697A US 5928981 A US5928981 A US 5928981A
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Prior art keywords
catalyst
aluminum silicate
catalyst composition
honeycomb carrier
zeolite
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Inventor
Jurgen Leyrer
Dieter Lindner
Egbert Lox
Thomas Kreuzer
Wilfried Muller
Rainer Domesle
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DMC2 DEGUSSA METALS
Umicore AG and Co KG
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Degussa Huels AG
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9445Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC]
    • B01D53/945Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC] characterised by a specific catalyst
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/80Mixtures of different zeolites
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/064Crystalline aluminosilicate zeolites; Isomorphous compounds thereof containing iron group metals, noble metals or copper
    • B01J29/068Noble metals
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/08Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the faujasite type, e.g. type X or Y
    • B01J29/10Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the faujasite type, e.g. type X or Y containing iron group metals, noble metals or copper
    • B01J29/12Noble metals
    • B01J29/126Y-type faujasite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/18Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the mordenite type
    • B01J29/20Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the mordenite type containing iron group metals, noble metals or copper
    • B01J29/22Noble metals
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/40Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the pentasil type, e.g. types ZSM-5, ZSM-8 or ZSM-11, as exemplified by patent documents US3702886, GB1334243 and US3709979, respectively
    • B01J29/42Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the pentasil type, e.g. types ZSM-5, ZSM-8 or ZSM-11, as exemplified by patent documents US3702886, GB1334243 and US3709979, respectively containing iron group metals, noble metals or copper
    • B01J29/44Noble metals
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/56Foraminous structures having flow-through passages or channels, e.g. grids or three-dimensional monoliths
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2229/00Aspects of molecular sieve catalysts not covered by B01J29/00
    • B01J2229/10After treatment, characterised by the effect to be obtained
    • B01J2229/16After treatment, characterised by the effect to be obtained to increase the Si/Al ratio; Dealumination
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/08Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the faujasite type, e.g. type X or Y
    • B01J29/084Y-type faujasite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/40Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the pentasil type, e.g. types ZSM-5, ZSM-8 or ZSM-11, as exemplified by patent documents US3702886, GB1334243 and US3709979, respectively
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02TCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
    • Y02T10/00Road transport of goods or passengers
    • Y02T10/10Internal combustion engine [ICE] based vehicles
    • Y02T10/12Improving ICE efficiencies

Definitions

  • the present invention relates to a catalyst for purifying the exhaust gases from diesel engines which contain one or more zeolites and at least one platinum group metal.
  • the present invention relates to a method of using the catalysts as described herein for the purification of diesel engine exhaust.
  • the exhaust gases from diesel engines contain carbon monoxide, unburnt hydrocarbons, nitrogen oxides and particles of soot as air pollutants.
  • the unburnt hydrocarbons include paraffins, olefins, aldehydes and aromatic compounds.
  • diesel exhaust gases contain a substantially higher proportion of long-chain paraffins which are difficult to oxidize.
  • diesel exhaust gases are substantially colder than the exhaust gases from gasoline engines and contain oxygen at a concentration between 3 and 10 volume percent.
  • the high oxygen concentration relates to the fact that diesel engines are operated with a large air/fuel ratio (kilograms of air to kilograms of fuel) of more than 18.
  • Gasoline engines in contrast, operate with an air/fuel ratio of 14.6, which enables stoichiometric combustion of hydrocarbons.
  • the exhaust gases from gasoline engines therefore contain virtually no oxygen.
  • the exhaust gas temperature in a diesel engine When operated under part-load, the exhaust gas temperature in a diesel engine is in the range 100 to 250° C. and achieves a maximum temperature of 500 to 650° C. only when operated under full load. In contrast, the exhaust gas temperature in a gasoline engine is between 400 and 450° C. under part-load and can rise to 1000° C. under full load.
  • VOC volatile organic components
  • DE 39 40 758 A1 describes a catalyst for the oxidative purification of exhaust gases from diesel engines with high conversion rates for hydrocarbons and carbon monoxides at low temperatures and an inhibited oxidizing effect toward nitrogen oxides and sulphur dioxide.
  • the active component in the catalyst consists of platinum, palladium, rhodium and/or iridium placed in contact with vanadium or an oxidic vanadium compound.
  • the active component is deposited into finely divided aluminum oxide, titanium oxide, silicon oxide, zeolite or mixtures of these.
  • the catalyst is applied in the form of a coating onto channels which allow the free passage of gases in a honeycomb shaped support made of ceramic or metal.
  • the light-off temperatures T 50% of this catalyst for carbon monoxide and hydrocarbons are in the range of 210 to 275° C. (The light-off temperatures T 50% are the temperatures of the exhaust gas at which just 50% of the pollutants are converted into harmless components.) At 350° C. the catalyst exhibits good conversion rates for carbon monoxide and hydrocarbons.
  • the catalyst allows nitrogen oxides to pass through virtually unchanged. Sulphur dioxide is oxidized to sulphur trioxide to only a very small extent. As a result of the dimininished oxidizing effect toward sulphur dioxide, this catalyst also leads to lower particle emissions than other oxidizing catalysts since less sulphate is available for adsorption onto the soot cores in the exhaust gases.
  • EP 0 427 970 A2 describes a catalyst for reducing the amount of nitrogen oxides in an oxidizing exhaust gas with an air/fuel ratio of 22.
  • the catalyst contains at least one zeolite with a molar ratio SiO 2 /Al 2 O 3 of more than 10 and pore diameters of 0.5 to 1 nm.
  • Platinum groups metals are deposited on the zeolites, wherein, for each platinum group metal, a minimum ratio by weight of metal to zeolite should not be undershot if good conversion rates for nitrogen oxides are still to be obtained even after aging of the catalyst.
  • DE 44 35 073 A1 describes a catalyst which contains a mixture of at least two zeolites with different pore diameters and also cerium oxide loaded with palladium.
  • the mixture of zeolites is used to adsorb the differently sized hydrocarbon molecules in the exhaust gas during the cold-start phase.
  • Palladium and cerium oxide are used to convert the adsorbed hydrocarbons into harmless constituents.
  • An object of the present invention is to provided an improved catalyst, as compared with the prior art, for purifying the exhaust gases from diesel engines, which is capable of oxidizing in particular long-chain paraffins which are difficult to oxidize in the exhaust gas at temperatures below 200° C., and simultaneously of reducing nitrogen oxides, despite the high oxygen content of the diesel exhaust gas.
  • a catalyst and method for purifying the exhaust gases from diesel engines wherein the catalyst comprises one or more zeolites and at least one platinum group metal.
  • the catalyst is characterized in that it also contains one or more additional metal oxides selected from the group consisting of aluminum silicate, aluminum oxide and titanium oxide, wherein the aluminum silicate has a ratio by weight of silicon dioxide to aluminum dioxide of 0.005 to 1.
  • the platinum group metal is deposited on only these additional metal oxides.
  • the catalyst contains, in addition to zeolites, other metal oxides which act as a support for the platinum groups metals. It is essential for purposes of this invention that the platinum group metals are deposited only on these additional metal oxides and not on the zeolites. Deposition of the platinum group metals on the zeolites leads to less active catalysts (see comparison Example C1).
  • Deposition of the platinum group metals on the additional metal oxides may be performed in a variety of ways. It is important that the method of deposition selected ensures production of the most uniformly and finely distributed deposit of platinum group metals possible on the additional metal oxides.
  • One possible method of deposition is to impregnate the additional metal oxides, before mincing with the zeolites, with a solution of soluble precursors of the platinum group metals.
  • Aqueous solutions are preferably used for this purpose.
  • Suitable precursors of platinum group metals are any common salts and complex salts of the same. Examples of such compounds are hexachloroplatinic acid, tetrachloroplatinic acid, diammine-dinitroplatinum(II), tetraammineplatinum(II) chloride, ammonium tetrachloroplatinate(II), ammonium hexachloroplatinate(IV), platinum ethylenediamine dichloride, tetraammineplatinum(II) nitrate, tetraammineplatinum(II) hydroxide, methylethanolamine platinum(II) hydroxide, platinum nitrate, palladium chloride, palladium nitrate, diamminedinitropalladium(II), tetraammine-palladium(II) hydroxide and hexachloroiridium acid.
  • the additional metal oxides are placed in contact with an aqueous solution of the platinum group metal(s), with constant stirring, so that a moist powder is produced.
  • the volume of solvent is selected to correspond to about 100 to 130, preferably 110% of the water absorption capacity of the metal oxide powder being impregnated.
  • the powder produced is calcined in air at 200 to 500, preferably 300° C. for 1 to 4 hours and then reduced in a hydrogen-containing stream of gas, preferably forming gas comprising 95 vol. % of nitrogen and 5 vol. % of hydrogen.
  • temperatures in the range of 300 to 600° C., preferably 500° are used. Reduction is complete after about 1 to 3 hours. Investigations using an electron microscope show that the platinum group metals deposited on the specific surface area of the metal oxides are finely distributed with crystallite sizes between 10 and 50 nm.
  • the additional metal oxides can be coated with a concentration of 0.01 to 5 wt. % of platinum group metal, with reference to the total weight of impregnated metal oxides.
  • the additional metal oxides may be coated with vanadium at the same time as with the platinum group metals or in any sequence with these.
  • further base metals such as nickel and copper may be deposited onto the additional metal oxides in order to have an effect on the catalytic activity of the platinum group metals. Soluble precursors of these metals are used for this purpose.
  • the additional metal oxides act as carrier material for the catalytically active platinum group metals.
  • Particularly suitable metal oxides are those which have a high specific surface area of more than 10 m 2 /g.
  • active aluminum oxides These have the crystal structures of the transition series of crystallo-graphic phases of aluminum oxide which are passed through when aluminum oxide/hydroxide such as, for example, gibbsite or boehmite, are calcined at up to more than 1000° C. In detail these are chi, eta, gamma, kappa, delta and theta-aluminum oxide.
  • Their specific surface areas may be several hundred square meters per gram.
  • These materials may be doped with, for example, rare earth oxides, in order to stabilize their specific surface areas.
  • Titanium oxides produced in a wet-chemical process largely possess the crystal structure of anatase and have specific surface areas of usually more than 50 m 2 /g. Titanium oxides produced by flame hydrolysis have a mixed structure of about 70% anatase and 30% rutile. The specific surface area of these so-called pyrogenic titanium oxides is about 50 m 2 /g.
  • aluminum silicate is preferably used as support material for the platinum group metals.
  • the material is a special aluminum silicate which has a ratio by weight of silicon dioxide to aluminum oxide of 0.005 to 1 and a very homogeneous distribution of aluminum oxide and silicon dioxide.
  • the crystal structure of this aluminum silicate in contrast to the zeolite, is boehmitic and becomes amorphous with increasing amounts of silicon dioxide.
  • the specific surface area of this aluminum silicate depending on the concentration of silicon dioxide, is 200 to 500 m 2 /g and exhibits exceptional surface area stability under the operating conditions obtained during purification of diesel exhaust gases. Table 1 shows these properties.
  • a specific concentration of metal crystallites is obtained per square meter of specific surface area of aluminum silicate for a given loading of the aluminum silicate (for example, 1.5 wt. % of Pt with reference to the total weight of aluminum silicate and platinum).
  • the crystallite concentration can be increased for the same loading by decreasing the specific surface area of the aluminum silicate.
  • Aluminum silicates of a given composition but with different specific surface areas can thus be prepared by calcination.
  • materials with a specific surface area greater than 100 m 2 /g are preferably used.
  • the platinum concentration in mg of Pt per square meter of specific surface are (in the freshly prepared state) is given in the last column of Table 1, calculated for the case of loading the aluminum silicate with 1 wt. % of platinum. It can be seen that, for a given composition of aluminum silicate (e.g., 95 Al 2 O 3 /5 SiO 2 ) and a given platinum loading (e.g., 1 wt. %), the platinum concentration on the specific surface area, and thus the crystallite concentration, can be affected by varying the specific surface area.
  • These aluminum silicates may optionally contain homogeneously incorporated elements which form oxides stable at high temperatures. Suitable elements are, for example, the rare earths such as lanthanum and cerium as well as zirconium and the alkaline earth metals, which are incorporated in the form of appropriate precursors. Concentrations of up to 10 wt. %, calculated as the oxide of these elements are preferred. High concentrations of alkali metals such as, for example, sodium have proven to be unsuitable. Particularly suitable aluminum silicates have a concentration of sodium, calculated as the oxide, of preferably less than 75 ppm.
  • a particularly suitable aluminum silicate is described in DE 38 39 580 C1.
  • the aluminum silicate is obtained by mixing an aluminum compound with a silicic acid compound in aqueous medium, drying and optionally calcining the product.
  • the aluminum compound used is a C 2 -C 20 -aluminum alcoholate which is hydrolyzed with water purified by passage through an ion exchanger.
  • 0.1 to 5.0 wt. % of orthosilicic acid, purified by passage through an ion exchanger are added to the hydrolysis water.
  • 0.1 to 5.0 wt. % of orthosilicic acid, purified by passage through an ion exchanger are added to the alumina/water mixture obtained by neutral hydrolysis.
  • This particularly preferred aluminum silicate may contain lanthanum oxide or also other rare earth oxides.
  • the zeolites used in the catalyst according to the invention must have a modulus greater than 10 in order to be sufficiently stable toward the acid components in the exhaust gas and to the maximum exhaust gas temperature.
  • Suitable zeolites are, for example, ZSM5, mordenite and dealuminized Y-zeolite (DAY). They may be used in the Na + or H + form.
  • Zeolites can be described by the general formula:
  • x is the so-called modulus of the zeolite and which is the molar ratio of silicon dioxide to aluminum oxide. Taking into account the molar weights, zeolites therefore have a ratio by weight of silicon dioxide to aluminum oxide of more than 1.18. Zeolites with a modulus of greater than 10, i.e., with a ratio by weight of silicon dioxide to aluminum oxide of greater than 5.9 are preferably used for the catalyst according to the invention. A ratio of this size ensures adequate stability of the characteristic crystal structure of the zeolites at the temperatures in diesel exhaust gases and at the concentrations of acid pollutants contained in them.
  • a zeolite mixture of at least two zeolites is used, one having a modulus of less than 50 and the other a modulus of more than 200. It has been shown that the broadest possible spectrum of modules for the zeolites used has an advantageous effect on the conversion rates of the pollutants.
  • a dealuminizing treatment it is possible to prepare zeolites of one structural type with a broad spectrum of modules.
  • the modulus of a ZSM5 zeolite with a stoichiometric composition, for example has a value of 5.
  • the modulus values can be adjusted to more than 1000. Similar behavior is shown by Y-zeolites and mordenite. Table 2 lists the properties of some zeolites which are suitable for the catalyst according to the invention.
  • a mixture of the 5 zeolites cited in Table 2 is preferably used in the catalyst according to the invention.
  • the ratio by weight of the zeolites with respect to each other can be varied over wide limits. However, a mixture with equal parts by weight of all the zeolites is mainly used.
  • a platinum activated aluminum silicate is combined with a zeolite mixture of a dealuminized Y-zeolite and a Na-ZSM5 zeolite whose moduli are greater than 120.
  • a particularly low light-off temperature for the conversion of carbon monoxide is obtained if an aluminum silicate with a specific surface area between 100 and 200 m 2 /g and with a platinum loading between 0.05 and 0.2 mg Pt/m 2 is used.
  • Particularly suitable for this purpose is an aluminum silicate with a SiO 2 content of about 5 wt.
  • the low light-off temperature under part-load is in the range 100 to 150° C. In this temperature range, a small reduction in the light-ff temperature represents a clear improvement in pollutant conversion.
  • the zeolite mixture is mixed with the catalytically activated additional metal oxides.
  • ratios by weight of metal oxides to zeolite mixture of 10:1 to 1:3, preferably 6:1 to 2:1, are used.
  • the zeolite mixture in the catalyst has the main task of storing the hydrocarbons in the exhaust gas at low exhaust gas temperatures ( ⁇ 150-200° C.) in order to release them again under operating conditions for the diesel engine with higher exhaust gas temperatures.
  • the desorbed hydrocarbons are partially oxidized by the catalytically activated additional metal oxides to give carbon monoxide and water.
  • the non-oxidized fraction of the hydrocarbons acts, in addition to carbon monoxide, as a reducing agent for the catalytic reduction of nitrogen oxides contained in the exhaust gas.
  • the resulting catalyst mixture can be processed by adding appropriate auxiliary agents such as inorganic binders (e.g., silica sol), pore producers, plasticizers and moistening agents in a known way to give molded items such as tablets and extrudates.
  • auxiliary agents such as inorganic binders (e.g., silica sol), pore producers, plasticizers and moistening agents in a known way to give molded items such as tablets and extrudates.
  • the catalyst is applied in the form of a coating to the internal walls of the flow channels in the honeycomb carriers.
  • honeycomb carrier volume For exhaust gas purification of diesel engines, amounts of coating of 50 to 400 g/l of honeycomb carrier volume are required.
  • the composition of the catalyst should be adjusted so that the catalytically active components on the additional metal oxides are present at a concentration of 0.01 to 5 g/l of honeycomb carrier volume.
  • the coating procedures required are known to a person skilled in the art.
  • the catalyst mixture of activated metal oxides and zeolite mixture are processed to give nan aqueous coating dispersion.
  • Silica sol for example, may be added to this dispersion as a binder.
  • the viscosity of the dispersion may be adjusted by suitable additives so that it is possible to apply the required amount of coating to the walls of the flow channels in a single working process. If this is not possible, the coating procedure may be repeated several times, wherein each freshly applied coating is fixed by an intermediate drying process.
  • the final coating is then dried at elevated temperature and calcined in air for a period of 1 to 4 hours at temperatures between 300 and 600° C.
  • the coating honeycomb carrier was then impregnated with an aqueous solution of tetra-ammine-platinum(II) hydroxide dried at 150° C. in air and calcined at 250° C.
  • the final catalyst contained 120 g of oxide and 1.77 g of platinum per liter of honeycomb carrier volume.
  • the open-celled honeycomb carrier consisted of cordierite with a diameter of 2.5 cm, a length of 7.6 cm and 62 cells or flow channels per cm 2 , the flow channels having a wall thickness of 0.2 mm.
  • a comparison catalyst was prepared as follows, in accordance with DE 39 40 758 A1, Example 18.
  • An aqueous coating dispersion with a solids content of 40% was made up.
  • the dispersion contained, with reference to dry substance, 60 wt. % of ⁇ -aluminum oxide (180 m 2 /g specific surface area) and 40 wt. % of titanium dioxide (50 m 2 /g specific surface area).
  • a honeycomb carrier was coated with the metal oxides by immersion in the coating dispersion and afterwards dried at 120° C. in the air. After calcining for 2 hours at 400° C., the coated honeycomb carrier was impregnated with an aqueous solution of tetraamineplatinum(II) hydroxide dried at 150° C.
  • the catalyst precursor obtained in this way was reduced for a period of 2 hours at 500° C. in a stream of forming gas (95% N 2 , 5% H 2 ) .
  • the final catalyst contained, per liter of honeycomb carrier volume, 64 g of titanium dioxide, 96 g of aluminum oxide, 5 g of vanadium oxide and 1.77 g of platinum.
  • a comparison catalyst was prepared as follows, in accordance with DE 39 40 758 A1.
  • An aqueous coating dispersion with a solids content of 40% was made up.
  • the dispersion contained, with reference to dry substance, 95 wt. % of ⁇ -aluminum oxide (180 m 2 /g specific surface area) and 5 wt. % of silicon dioxide (100 m 2 /g specific surface area).
  • a honeycomb carrier was coated with the metal oxides by immersion in the coating dispersion and afterwards dried at 120° C. in air. After calcining for 2 hours at 400° C., the coated honeycomb carrier was impregnated with an aqueous solution of hexachloroplatinic acid, dried at 150° C.
  • the catalyst precursor obtained in this way was reduced for 2 hours at 500° C. in a stream of forming gas (98% N 2 , 5% H 2 ).
  • the final catalyst contained, per liter of honeycomb carrier, 200 g of oxide and 1.77 g of platinum.
  • a comparison catalyst was prepared as follows, in accordance with DE 44 35 073 A1, Example 13. First, cerium dioxide with a specific surface area of 105 m 2 /g was impregnated with palladium. For this, the cerium dioxide was placed in contact with an aqueous solution of tetraammine-platinum(II) nitrate, with constant stirring, so that a moist powder was produced. After drying for two hours at 120° C. in air, the powder produced was calcined for 2 h at 300° C. in air. The Pd-cerium oxide powder contained, with reference to the total weight, 1.47 wt. % of palladium.
  • An aluminum silicate with 5 wt. % of silicon dioxide (spec. surface area 286 m 2 /g; see Table 1) was activated with platinum for the catalyst according to the invention.
  • the aluminum silicate was placed in contact with an aqueous solution of tetraammineplatinum(II) hydroxide, with constant stirring, so that a moist powder was produced.
  • the powder produced was calcined at 2 h at 300° C. in air.
  • Reduction in a stream of forming gas (95 vol. % N 2 and 5 vol. % H 2 ) was performed at 500° C. for a period of 2 h.
  • the Pt-aluminum silicate powder contained, with reference to the total weight, 1.47 wt. % of platinum.
  • This honeycomb carrier was coated with an amount of 180 g of oxides per liter of honeycomb carrier volume, by immersion in the coating dispersion. The coating was dried for 2 hours at 120° C. in air and then calcined for 2 h at 500° C. The final catalyst contained, per liter of catalyst volume, 1.77 g of platinum.
  • a further catalyst in accordance with Example 1 was made up. Instead of the zeolite mixture, only Na-ZSM5 (x>1000) in amount of 33 wt. %, with reference to the total weight of catalyst mixture, was used.
  • the aluminum silicate was coated with 2.94 wt. % of platinum.
  • the precise composition of the catalyst can be obtained from Table 4.
  • Example 7 Another catalyst analogous to Example 7 was made up, but with a ratio by weight of Pt-aluminum silicate to zeolite mixture of 5:1.
  • a catalyst according to Example 13 with 0.18 g of Pt per liter of honeycomb carrier was also coated, along 30% of its length, with the coating dispersion for the catalyst in Example 9.
  • the additional coating was applied at a concentration of 39 g/l of honeycomb carrier volume.
  • the final catalyst contained 209 g of oxides per liter of honeycomb carrier and had a concentration of 0.72 g Pt/l.
  • Example 15 The additional coating on the catalyst in Example 15 was applied each time to 15% of the length of the honeycomb carrier starting from a front face of the honeycomb carrier.
  • a catalyst was made up according to Example 10 with 1.41 g Pt/l of honeycomb carrier, but using only 60 g/dm 3 of aluminum silicate.
  • a catalyst with 140 g/l Pt-aluminum silicate and 100 g/l of zeolite mixture was made up.
  • the platinum content of the Pt-aluminum silicate was 1.0 wt. %.
  • the final catalyst contained 1.41 g Pt/l.
  • a catalyst was prepared according to Example 10. An aqueous solution of hexachloroplatinic acid was used to activate the aluminum silicate.
  • a catalyst was prepared according to Example 10. An aqueous solution of platinum (II) nitrate was used to activate the aluminum silicate.
  • a catalyst was prepared according to Example 9. Palladium, incorporated using an aqueous solution of palladium(II) nitrate, was used to activate the aluminum silicate.
  • a catalyst was prepared according to Example 1. A mixture of platinum and rhodium in the ratio of 5:1 was used to activate the aluminum silicate. Hexachloroplatinic acid was used as a precursor for platinum and rhodium(III) chloride was used as a precursor for rhodium.
  • a catalyst according to Example 1 was prepared. A mixture of platinum, palladium and rhodium in the ratio of 10:1:3 was used to activate the aluminum silicate. Tetraamineplatinum(II) hydroxide was used as a precursor for platinum, palladium(II) nitrate as a precursor for palladium and rhodium(II) nitrate as a precursor for rhodium.
  • a catalyst according to Example 10 was prepared.
  • An aqueous solution of methylethanoloamine-platinum(II) hydroxide was used to activate the aluminum silicate.
  • a catalyst according to Example 1 was prepared. Differently from Example 1, the aluminum silicate activated with platinum was not reduced in a stream of forming gas, but was only calcined in air for 2 hours at 600° C.
  • a catalyst according to Example 1 was prepared, but the Pt-aluminum silicate was not dried and calcined or reduced after impregnation, but was mixed immediately with zeolite mixture and processed to form a coating dispersion.
  • the aluminum silicate was dispersed in an aqueous solution of platinum (II) nitrate. Then the pH of the dispersion was increased to 9 by adding an aqueous, concentrated ammonia solution. Then the zeolite mixture was stirred into the dispersion. The final dispersion had a solids content of 40 wt. %.
  • a catalyst according to Example 28 was prepared. Instead of platinum(II) nitrate, an aqueous solution of tetraammineplatinum (II) nitrate was used. Adjustment of the pH to 2 was achieved by adding a saturated aliphatic monocarboxylic acid.
  • a catalyst according to Example 17 was prepared. Instead of the ceramic honeycomb carrier of cordierite, a likewise open-celled, honeycomb-shaped, metal carrier with a diameter of 2.5 cm, a length of 7.5 cm and 62 cells or flow channels per cm 2 , the flow channels having a wall thickness of 0.4 mm, was used.
  • a catalyst according to Example 9 was prepared. Instead of the aluminum silicate, a ⁇ -aluminum oxide with a specific surface area of 188 m 2 /g was used.
  • a catalyst according to Example 9 was prepared. Instead of the aluminum silicate, titanium oxide with a specific surface area of 95 m 2 /g was used.
  • a catalyst according to Example 1 was made up, but with the following modifications.
  • An aluminum silicate with a specific surface area reduced to 153 m 2 /g by calcination was used (see Table 1).
  • This material was impregnated with methylethanolamine platinum(II) hydroxide in the same way as in Example 26.
  • the zeolite mixture selected was a mixture of DAY and Na-ZSM5.
  • the ratio by weight of aluminum silicate to zeolites was adjusted to 6:1.
  • the amount of coating per liter of honeycomb carrier volume was 140 g.
  • the catalyst was finally reduced for 2 hours in a stream of forming gas at 500°0 C.
  • the final catalyst contained 1.36 g of platinum per liter of catalyst volume.
  • a catalyst according to Example 33 was prepared.
  • An aqueous solution of tetraammineplatinum(II) nitrate was used to activate the aluminum silicate.
  • a catalyst according to Example 34 was prepared.
  • An aluminum silicate with 5 wt. % of silicon dioxide and a specific surface area of 212 m 2 /g (see Table 1) was used as support oxide.
  • a catalyst according to Example 34 was prepared.
  • An aluminum silicate with 5 wt. % of silicon dioxide and a specific surface area of 320 m 2 /g (see Table 1) was used as support oxide.
  • a catalyst according to Example 36 was prepared.
  • An aluminum silicate with 10 wt. % of silicon dioxide and a specific surface area of 163 m 2 /g (see Table 1) was used as support oxide.
  • the catalytic activity of the exhaust gas purification catalysts in the preceding examples was measured in a synthesis gas unit. Using this unit, it is possible to simulate all the gaseous exhaust gas components present in the actual exhaust gas from a diesel of a gasoline engine.
  • the test conditions selected and the model gas composition are given in Table 5. Normal- hexadence, trivial name cetane, which is known as a reference substance for determining the ignition performance of diesel fuels, was used as the hydrocarbon component. Considerable amounts of this long-chain, aliphatic compound are also found in actual diesel exhaust gas.
  • the exhaust gas was heated at a rate of 15° C./min.
  • the conversion of nitrogen oxides was determined at an exhaust gas temperature of 200° C.
  • German priority application 196 14 540.6 is relied on and incorporated herein by reference.

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Families Citing this family (22)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4983366A (en) * 1987-09-21 1991-01-08 Degussa Aktiengesellschaft Method for the catalytic conversion of waste gases containing hydrocarbon, halogenated hydrocarbon and carbon monoxide
EP0432534A1 (de) * 1989-12-09 1991-06-19 Degussa Ag Katalysator zur Reinigung der Abgase von Dieselmotoren
US5085762A (en) * 1990-07-05 1992-02-04 Mobil Oil Corporation Catalytic cracking of hydrocarbons
US5089459A (en) * 1989-03-29 1992-02-18 Teijin Petrochemical Industries, Ltd. Catalyst composition, process for cracking non-aromatic hydrocarbons and process for isomerizing c8 aromatic hydrocarbons
US5118889A (en) * 1991-10-21 1992-06-02 Shell Oil Company Process for preparing allyl chloride
EP0559021A2 (de) * 1992-03-04 1993-09-08 Degussa Aktiengesellschaft NOx-Verminderung im mageren Abgas von Kraftfahrzeugmotoren
EP0582971A1 (de) * 1992-08-10 1994-02-16 Degussa Aktiengesellschaft Verfahren zur katalytischen Autoabgasreinigung mit verbessertem Kaltstartverhalten
DE4239875A1 (de) * 1992-11-27 1994-06-01 Degussa Abgasreinigungssystem zur Verminderung der Kohlenwasserstoff-Emissionen während des Kaltstarts von Verbrennungskraftmaschinen
DE4435073A1 (de) * 1993-09-30 1995-04-06 Mazda Motor Kohlenwasserstoffadsorptionsmittel zur Abgasreinigung, Abgasreinigungskatalysator und Abgasreinigungsvorrichtung
EP0706817A2 (de) * 1994-10-15 1996-04-17 Degussa Aktiengesellschaft Verfahren zur gleichzeitigen Verminderung der im Abgas einer Verbrennungskraftmaschine enthaltenen Kohlenwasserstoffe, Kohlenmonoxid und Stickoxide
EP0716877A1 (de) * 1994-12-13 1996-06-19 Johnson Matthey Public Limited Company Katalytische Reinigung von Motorabgas

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE4213018C1 (de) * 1992-04-21 1993-12-09 Degussa Katalysator zur oxidativen Reinigung der Abgase von Dieselmotoren

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4983366A (en) * 1987-09-21 1991-01-08 Degussa Aktiengesellschaft Method for the catalytic conversion of waste gases containing hydrocarbon, halogenated hydrocarbon and carbon monoxide
US5089459A (en) * 1989-03-29 1992-02-18 Teijin Petrochemical Industries, Ltd. Catalyst composition, process for cracking non-aromatic hydrocarbons and process for isomerizing c8 aromatic hydrocarbons
EP0432534A1 (de) * 1989-12-09 1991-06-19 Degussa Ag Katalysator zur Reinigung der Abgase von Dieselmotoren
US5085762A (en) * 1990-07-05 1992-02-04 Mobil Oil Corporation Catalytic cracking of hydrocarbons
US5118889A (en) * 1991-10-21 1992-06-02 Shell Oil Company Process for preparing allyl chloride
EP0559021A2 (de) * 1992-03-04 1993-09-08 Degussa Aktiengesellschaft NOx-Verminderung im mageren Abgas von Kraftfahrzeugmotoren
EP0582971A1 (de) * 1992-08-10 1994-02-16 Degussa Aktiengesellschaft Verfahren zur katalytischen Autoabgasreinigung mit verbessertem Kaltstartverhalten
DE4239875A1 (de) * 1992-11-27 1994-06-01 Degussa Abgasreinigungssystem zur Verminderung der Kohlenwasserstoff-Emissionen während des Kaltstarts von Verbrennungskraftmaschinen
DE4435073A1 (de) * 1993-09-30 1995-04-06 Mazda Motor Kohlenwasserstoffadsorptionsmittel zur Abgasreinigung, Abgasreinigungskatalysator und Abgasreinigungsvorrichtung
EP0706817A2 (de) * 1994-10-15 1996-04-17 Degussa Aktiengesellschaft Verfahren zur gleichzeitigen Verminderung der im Abgas einer Verbrennungskraftmaschine enthaltenen Kohlenwasserstoffe, Kohlenmonoxid und Stickoxide
EP0716877A1 (de) * 1994-12-13 1996-06-19 Johnson Matthey Public Limited Company Katalytische Reinigung von Motorabgas

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6220022B1 (en) 1997-03-06 2001-04-24 Degussa Ag Catalyst system for the treatment of exhaust gases from diesel engines
US6191061B1 (en) * 1997-04-23 2001-02-20 Toyota Jidosha Kabushiki Kaisha Method of purifying exhaust gas and catalyst for purifying exhaust gas
US6147023A (en) * 1997-10-28 2000-11-14 Toyota Jidosha Kabushiki Kaisha Hydrocarbon-adsorbent
US6342465B1 (en) * 1997-12-04 2002-01-29 Dmc2 Degussa Metals Process for preparing a catalyst
US6534439B2 (en) * 1998-07-04 2003-03-18 Degussa-Huls Aktiengesellschaft Catalyst for reducing nitrogen oxides in oxidizing and reducing atmospheres
US6953762B2 (en) * 1998-12-25 2005-10-11 Tosoh Corporation Combustion catalysts and processes for removing organic compounds
US7052663B2 (en) 1998-12-25 2006-05-30 Tosoh Corporation Combustion catalysts and processes for removing organic compounds
US20020155051A1 (en) * 1998-12-25 2002-10-24 Tosoh Corporation Combustion catalysts and processes for removing organic compounds
US6475951B1 (en) * 1999-02-06 2002-11-05 Degussa-Huls Aktiengessellschaft Catalyst material
KR20010037201A (ko) * 1999-10-14 2001-05-07 이계안 디젤 자동차용 촉매
US6294389B1 (en) * 1999-11-01 2001-09-25 General Motors Corporation Furnace for an engine exhaust measurement system
US6818195B2 (en) * 2000-02-07 2004-11-16 Tosoh Corporation Combustion catalyst and process for removing organic compounds
US20030153453A1 (en) * 2000-08-08 2003-08-14 Cataler Corporation Catalyst for purifying exhaust gas
US6767855B2 (en) * 2000-08-08 2004-07-27 Cataler Corporation Catalyst for purifying exhaust gas
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US6691509B2 (en) 2001-01-27 2004-02-17 Umicore Ag & Co. Kg Process for regenerating the catalytic activity of a catalyst that is located in the exhaust gas line of a diesel engine and that has at least one oxidizing function
US7563744B2 (en) * 2001-08-09 2009-07-21 Umicore Ag & Co. Kg Catalyst featuring silicone dioxide based support material for the purification of exhaust gases
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US6908874B2 (en) 2001-09-14 2005-06-21 Rothmans, Benson & Hedges Inc. Process for making metal oxide-coated microporous materials
US20050170948A1 (en) * 2001-09-14 2005-08-04 Rothmans, Benson & Hedges Inc. Process for making metal oxide-coated microporous materials
US20030114298A1 (en) * 2001-09-14 2003-06-19 Rothmans, Benson & Hedges Inc. Process for making metal oxide-coated microporous materials
US7531477B2 (en) 2001-09-14 2009-05-12 Rothmans, Benson & Hedges Inc. Process for making metal oxide-coated microporous materials
US7740819B2 (en) 2002-02-26 2010-06-22 Nippon Shokubai Co., Ltd. Process for purification of exhaust gases and catalyst used for purification of exhaust gases in this process
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US20030170160A1 (en) * 2002-02-26 2003-09-11 Atsushi Morita Process for purification of exhaust gases and catalyst used for purification of exhaust gases in this process
US20080029113A1 (en) * 2002-03-15 2008-02-07 Snaidr Stanislav M Low sidestream smoke cigarette with combustible paper having a modified ash
US20060248877A1 (en) * 2002-11-08 2006-11-09 Emitec Gesellschaft Für Emissionstechnologie Mbh Exhaust system and method for operating the same
US7481041B2 (en) * 2002-11-08 2009-01-27 Emitec Gesellschaft Fuer Emissionstechnologie Mbh Exhaust system and method for operating the same
US7763560B2 (en) 2003-05-06 2010-07-27 Ict Co., Ltd Catalyst for purifying diesel engine exhaust gas and method for production thereof
US20040224837A1 (en) * 2003-05-06 2004-11-11 Makoto Horiuchi Catalyst for purifying diesel engine exhaust gas and method for production thereof
DE10322148B4 (de) * 2003-05-16 2006-11-02 Umicore Ag & Co. Kg Abgasreinigungsanlage mit Partikelfilter und Verfahren zu ihrem Betrieb mit verbesserter Regeneration des Partikelfilters
US20090255241A1 (en) * 2003-08-05 2009-10-15 Basf Catalysts Llc Method of Forming a Catalyzed SCR Filter
US8899023B2 (en) 2003-08-05 2014-12-02 Basf Corporation Catalyzed SCR filter and emission treatment system
US9039983B1 (en) 2003-08-05 2015-05-26 Basf Corporation Catalyzed SCR filter and emission treatment system
US9039984B1 (en) 2003-08-05 2015-05-26 Basf Corporation Catalyzed SCR filter and emission treatment system
US20080132405A1 (en) * 2003-08-05 2008-06-05 Joseph Allan Patchett Catalyzed SCR Filter and Emission Treatment System
US9040006B1 (en) 2003-08-05 2015-05-26 Basf Corporation Catalyzed SCR filter and emission treatment method
US10857529B2 (en) 2003-08-05 2020-12-08 Basf Corporation Catalyzed SCR filter and emission treatment system
US9039982B2 (en) 2003-08-05 2015-05-26 Basf Corporation Catalyzed SCR filter and emission treatment system
US7902107B2 (en) 2003-08-05 2011-03-08 Basf Corporation Catalyzed SCR filter and emission treatment system
US10518254B2 (en) 2003-08-05 2019-12-31 Basf Corporation Catalyzed SCR filter and emission treatment system
US9032709B2 (en) 2003-08-05 2015-05-19 Basf Corporation Method of forming a catalyzed selective catalytic reduction filter
US10258972B2 (en) 2003-08-05 2019-04-16 Basf Corporation Catalyzed SCR filter and emission treatment system
US8122603B2 (en) 2003-08-05 2012-02-28 Basf Corporation Method of forming a catalyzed selective catalytic reduction (SCR) filter
US9757717B2 (en) 2003-08-05 2017-09-12 Basf Corporation Method for disposing SCR composition on a wall flow monolith
US20070137184A1 (en) * 2003-08-05 2007-06-21 Basf Catalysts Llc Catalyzed SCR Filter and Emission Treatment System
US9144795B2 (en) 2003-08-05 2015-09-29 Basf Corporation Catalyzed SCR filter and emission treatment system
US9517456B2 (en) 2003-08-05 2016-12-13 Basf Corporation Catalyzed SCR filter and emission treatment system
US9517455B2 (en) 2003-08-05 2016-12-13 Basf Corporation Catalyzed SCR filter and emission treatment system
US9121327B2 (en) 2003-08-05 2015-09-01 Basf Corporation Catalyzed SCR filter and emission treatment system
US7541012B2 (en) * 2004-07-07 2009-06-02 The Hong Kong University Of Science And Technology Catalytic material and method of production thereof
US20060009354A1 (en) * 2004-07-07 2006-01-12 Hong Kong University Of Science And Technology Catalytic material and method of production thereof
EP1779927A2 (de) * 2005-10-20 2007-05-02 N.E. Chemcat Corporation Abgasbehandlungskatalysator und seine Verwendung zur Behandlung von Dieselabgasen
EP1779927A3 (de) * 2005-10-20 2007-07-04 N.E. Chemcat Corporation Abgasbehandlungskatalysator und seine Verwendung zur Behandlung von Dieselabgasen
US20080286177A1 (en) * 2007-05-18 2008-11-20 Tribute Creations, Llc Reactor with differentially distributed catalytic activity
US8420035B2 (en) 2007-11-28 2013-04-16 Sued-Chemie Ip Gmbh & Co. Kg Coating composition for diesel oxidation catalysts
US20110044871A1 (en) * 2007-11-28 2011-02-24 Sud-Chemie Ag Coating composition for diesel oxidation catalysts
US20110120093A1 (en) * 2008-04-24 2011-05-26 Stephan Eckhoff Process and apparatus for purifying exhaust gases from an internal combustion engine
US8445403B2 (en) 2008-06-19 2013-05-21 Umicore Ag & Co. Kg Oxidation catalyst for commercial vehicles comprising a diesel motor
US20110229392A1 (en) * 2008-06-19 2011-09-22 Umicore Ag & Co. Kg Oxidation catalyst for commercial vehicles comprising a diesel motor
US10265689B2 (en) 2009-03-30 2019-04-23 Clariant Produkte (Deutschland) Gmbh Age-resistant catalyst for oxidation of NO to NO2 in exhaust streams
US8246923B2 (en) 2009-05-18 2012-08-21 Umicore Ag & Co. Kg High Pd content diesel oxidation catalysts with improved hydrothermal durability
US20100290964A1 (en) * 2009-05-18 2010-11-18 Southward Barry W L HIGH Pd CONTENT DIESEL OXIDATION CATALYSTS WITH IMPROVED HYDROTHERMAL DURABILITY
US8557203B2 (en) 2009-11-03 2013-10-15 Umicore Ag & Co. Kg Architectural diesel oxidation catalyst for enhanced NO2 generator
US20110099975A1 (en) * 2009-11-03 2011-05-05 Owen Herman Bailey Architectural diesel oxidation catalyst for enhanced no2 generator
US9011783B2 (en) 2009-11-12 2015-04-21 Umicore Ag & Co. Kg Diesel oxidation catalyst
RU2574404C2 (ru) * 2010-02-01 2016-02-10 Джонсон Мэтти Плс Тройной катализатор, содержащий экструдированную твердую массу
US9433899B2 (en) 2012-04-05 2016-09-06 Umicore Ag & Co. Kg Method for removing carbon monoxide and hydrocarbons from the exhaust gas of lean-burn internal combustion engines
US9757712B2 (en) 2013-10-22 2017-09-12 Umicore Ag & Co. Kg Catalyst for the oxidation of CO and HC at low temperatures
RU2576568C2 (ru) * 2013-12-30 2016-03-10 Федеральное государственное бюджетное учреждение науки Институт химии Дальневосточного отделения Российской академии наук (ИХ ДВО РАН) Способ получения прекурсора на основе гидратированного диоксида титана с наноразмерными металлическими частицами палладия для каталитически активного покрытия на инертном носителе

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DE19614540A1 (de) 1997-10-16
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MX9702631A (es) 1997-10-31
CN1091002C (zh) 2002-09-18

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